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Bird–window collisions

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why nocturnally migrating birds are attracted to artificial lights, we do know that birds rely on a variety of cues for migration, with the orientation of the stars being a major reference for nocturnal migrants. It is therefore speculated that these artificially illuminated areas conceal the visual navigation cues that these birds rely on, resulting in them becoming disoriented. This hypothesis has been well supported by several observations of birds being attracted to and disoriented by lights, particularly in conditions of poor-visibility, which makes them more susceptible to colliding with buildings.
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high levels of mortality at large commercial buildings. Further, buildings located in more developed areas experience fewer collisions than those in less-developed areas, due to effects of proximity to forested patches. This is most noticeable in residences across a rural-urban gradient, where per-building mortality rates are higher in rural areas. However, despite causing the lowest total mortality, more recent studies reveal that high-rise buildings have the highest median annual mortality rates.
142:, which make up a disproportionately high amount of window collisions in the fall and winter, are thought to be susceptible due to their flocking behaviors. During these months, waxwings forage in large flocks to more efficiently search for berries. It is thought that this seasonal increase in collisions is due to their increased concentration of movement, and perhaps because flocking birds are less attentive to their surroundings, opting to follow the lead bird in the flock. 138:
especially attracted to lit structures. Warblers, thrushes, and vireos are known to make quick flight movements through densely vegetated areas, and are thought to be heavily guided by light in flight, which could account for this susceptibility to light disruption. Further, some of these species, such as thrushes and ovenbirds, spend more time near the ground, which is another characteristic shared among many common window-strike victims. Species like
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lift for larger, soaring raptors, which can lead to collisions with skyscrapers. Other factors, including humidity and air temperature, can also influence flight altitudes of birds in ways that influence risk of collision. Some of the highest reports of bird fatalities from window collisions have occurred when migrating passerines began their journey in good weather conditions, but hit a cold front which forced them to lower altitudes.
215: 181: 102:, indicating that some birds are more vulnerable to collisions than others. This most likely depends on differing morphology and physical flight characteristics of birds, but more subtle differences between groups are also thought to contribute to differences in vulnerability. Examples include differences in vision, degree of flocking, flight behaviors, and more specific life history traits, such as provisioning of young. 206:
there are increases in bird collisions during fall and spring migrations due to greater movement in bird populations, and because birds are less familiar with the landscape along their migratory routes. Additionally, fatalities in fall migration are consistently greater than in spring migration, which is likely due to a larger proportion of young, relatively inexperienced birds.
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Bird-Friendly Building Design Ordinance. On the Federal level the Federal Bird-Safe Buildings Act of 2011 calls for each public building constructed, acquired, or altered by the General Services Administration (GSA) to incorporate bird-safe building materials and design features. The legislation would require GSA to take similar actions on existing buildings, where practicable.
257:(UV) signals to make windows appear visible to birds, while once one of the most common means of combatting this issue, is no longer recommended by experts. This is because while some birds can see UV light, not all can. Other solutions include window film (as long as it is placed on the exterior of the glass) and ceramic frit glass (glass with 197:
areas that support high densities of birds. Urban greenspaces are one example, used by many species of songbird for foraging, breeding, or as migratory stopover sites. We may also see channeling effects at a fine scale, when architectural corridors guide bird flight paths into areas of increased collision risk.
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Weather conditions influence bird flight behavior in ways that make them more or less susceptible to collisions. Conditions which reduce visibility, such as fog, rain, or snow, can disorient birds, especially those that migrate at night and rely on visual cues. Low wind speeds can also result in poor
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The number of observed bird fatalities caused by any given building varies greatly across a spatial scale. There is a positive correlation between the number of collisions which occur at a building and the amount of the building surface area which is covered with windows. This is heavily evidenced by
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In addition, birds may also be impacted by bright lights at nights as they have extra-retinal photoreceptors that are disoriented by the reflection of light from these buildings. Mitigating the amount of light emitted from glass surfaces at night, such as windows, can reduce the amount of fatal bird
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The presence and height of vegetation surrounding a building is also positively correlated with bird mortalities. This is because highly reflective windows create an illusion of vegetation that birds can fly into, and birds are unable to recognize the cues of a window the way that humans do. A study
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Further, governments of Canada and the United States have recently introduced legislation to make new and existing buildings bird friendly. Examples include Toronto's Bird-Friendly Development Guidelines, Chicago's Design Guide For Bird-Safe Buildings New Construction And Renovation, and Evanston's
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dots). Windows can also be covered with decals spaced no more than 5 cm horizontally or 10 cm vertically to prevent collisions. It has been found that silhouettes of predatory birds posted on windows do not significantly decrease collision rates. This is because there is too much exposed
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Bird mortality rates increase with the amount of light that is emitted from a given building and bird species that migrate at night are particularly vulnerable to collisions, which is thought to be attributed to fatal entrapment by light-emitting structures. While there are various explanations for
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Collisions appear to happen less frequently during the winter and more frequently during peak migration periods, though seasonal patterns of mortality are difficult to detect due to limited availability of studies that survey collisions throughout the year. However, it is generally understood that
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Building layout, orientation, and spacing within a city is another a contributing factor to bird-window collisions, as we often see topographical features within urban planning that channel or concentrate bird movements. Structures are at a greater risk of causing bird fatalities when located near
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In New York City, where an estimated 230,000 birds collide with buildings each year, New York's Bird Friendly-Buildings Act required new and existing building be bird friendly effective Jan 1, 2012. In December 2019, a bill passed mandating that the lowest 75 feet of new buildings, and structures
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being the most notable. The reason for these species' vulnerability is not well understood, but it is speculated that species-specific behaviors are a likely contributor, as other factors like flight altitude differ greatly between these groups. Many of these birds have been documented as being
274:'s Project Safe Flight, which all have documented thousands of bird collisions due to human-made structures. Monitoring programs such as these are becoming more and more common at a local level, and rely heavily on participation from volunteer groups. 53:) are a problem in both low- and high-density areas worldwide. Birds strike glass because reflective or transparent glass is often invisible to them. It is estimated that between 100 million and 1 billion birds are killed by collisions in the 193:
conducted in Manhattan found support for the hypothesis that most collisions occur during daytime hours, when birds are foraging for food, due to the high number of collisions that occurred at windowed exteriors incorporating vegetation.
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The issue of bird-window collisions has become more prevalent as wild habitat is lost. It has intensified as landscaping and exterior glass continue to become more popular. However, due to differences within the
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above a green roof, must use materials such as patterned glass which are visible to flying birds. Compliance with these new standards will also be required for building renovations beginning in December 2020.
1205:"S4204-2011 - NY Senate Open Legislation - Enacts the "bird-friendly buildings act" to require use of bird-friendly building materials and design features in buildings - New York State Senate" 988:
Barrios, Luis; Rodríguez, Alejandro (12 February 2004). "Behavioural and environmental correlates of soaring-bird mortality at on-shore wind turbines: Bird mortality at wind power plants".
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glass, which the bird can try to fly through. Treatments placed on the inside of windows are not effective either, because they typically do not diminish the glare or reflection.
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Klem, Daniel (1991). "Glass and bird kills: an overview and suggested planning and design methods of preventing a fatal hazard". In Adams, Lowell W.; Leedy, Daniel L. (eds.).
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Shochat, Eyal; Lerman, Susannah; Fernández-Juricic, Esteban (2015). "Birds in Urban Ecosystems: Population Dynamics, Community Structure, Biodiversity, and Conservation".
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Many bird-rescue organizations have come about in recent years. Examples include Chicago Bird Collision Monitors, Toronto's Fatal Light Awareness Program (FLAP), and
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There are also patterns of species mortality across different building types, which are most likely due to differences in flight behavior. For instance,
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Hager, Stephen B.; Trudell, Heidi; McKay, Kelly J.; Crandall, Stephanie M.; Mayer, Lance (September 2008). "Bird density and mortality at windows".
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Instructions to make your own Acopian BirdSavers to prevent birds from flying into windows - tested by Muhlenburg College's Center for Ornithology
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Lao, Sirena; Robertson, Bruce A.; Anderson, Abigail W.; Blair, Robert B.; Eckles, Joanna W.; Turner, Reed J.; Loss, Scott R. (January 2020).
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Drewitt, Allan L.; Langston, Rowena H.W. (June 2008). "Collision Effects of Wind-power Generators and Other Obstacles on Birds".
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Hager, Stephen B.; Cosentino, Bradley J.; McKay, Kelly J.; Monson, Cathleen; Zuurdeeg, Walt; Blevins, Brian (9 January 2013).
74:, built environments, time of year, and other effects, there is great variation in the nature and frequency of collisions. 737:
Gelb, Yigal; Delacretaz, Nicole (September 2009). "Windows and Vegetation: Primary Factors in Manhattan Bird Collisions".
245: 871:"Pre-migration artificial light at night advances the spring migration timing of a trans-hemispheric migratory songbird" 971:
Richardson, W John (2000). "Bird Migration and Wind Turbines: Migration Timing, Flight Behavior, and Collision Risk".
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Summary report on the Bird Friendly Building Program: effect of light reduction on collision of migratory birds
172:, are killed at relatively low rates, further indicating that species mortality is not dependent on density. 1308: 1298: 599:"Bird–building collisions in the United States: Estimates of annual mortality and species vulnerability" 555: 271: 146: 1151: 1282: 1303: 691: 680:"Window Area and Development Drive Spatial Variation in Bird-Window Collisions in an Urban Landscape" 488: 122: 531: 1169: 158: 99: 1128: 1078: 953: 906: 754: 655: 620: 512: 168:
It has been observed that many species which are very high in abundance in urban areas, such as
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Studies analyzing window collisions across greater spatial scales reveal interesting trends in
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annually, and an estimated 16 to 42 million birds are likewise killed each year in
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Collision course: the hazards of lighted structures and windows to migrating birds
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Loss, Scott R.; Will, Tom; Loss, Sara S.; Marra, Peter P. (1 February 2014).
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Basilio, Lay G.; Moreno, Daniele J.; Piratelli, Augusto J. (2020-03-16).
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There are several methods of preventing bird-window strikes. The use of
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Machtans, Craig S.; Wedeles, Christopher H. R.; Bayne, Erin M. (2013).
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Windows fitted with a dotted grid pattern to prevent bird collisions
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Proceedings of the National Avian - Wind Power Planning Meeting III
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Smith, Reyd A.; Gagné, Maryse; Fraser, Kevin C. (January 2021).
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Klem, Daniel (June 2009). "Preventing Bird–Window Collisions".
1272: 349:. National Institute for Urban Wildlife. pp. 99–104. 1262: 347:Wildlife Conservation in Metropolitan Environments 218:Haze created by light pollution in an urban center 774:"Main causes of bird-window collisions: a review" 560:: CS1 maint: DOI inactive as of September 2024 ( 836:Berthold, P. (1990). "Genetics of Migration". 153:are most at risk at low-rises and high-rises, 34:Imprint from where a bird has struck a window 8: 1231:"NYC Is Making Its Buildings Bird-Friendly" 481:Annals of the New York Academy of Sciences 228:collisions with buildings and structures. 1009: 789: 713: 703: 614: 387: 778:Anais da Academia Brasileira de Ciências 244: 29: 532:"'Tunnel Fliers' and Window Fatalities" 407:. Agronomy Monographs. pp. 75–86. 320: 673: 671: 669: 553: 94:) that died after flying into a window 1056: 1054: 592: 590: 588: 586: 577:Birds and powerlines, Quercus, Madrid 474: 472: 470: 468: 466: 442: 440: 438: 436: 434: 432: 340: 338: 121:are among the most susceptible, with 7: 184:Nearby vegetation reflected in glass 1170:"News List | City of Evanston" 25: 1229:Poon, Linda (December 13, 2019). 1063:The Wilson Journal of Ornithology 817:. Fatal Light Awareness Program. 640:The Wilson Journal of Ornithology 530:Snyder, L. L. (1 November 1946). 1207:. M.nysenate.gov. Archived from 1002:10.1111/j.1365-2664.2004.00876.x 1241:from the original on 2019-12-13 447:Ogden, Lesley J. Evans (1996). 1273:Acopian Center for Ornithology 813:Evans Ogden, Lesley J (2002). 451:. World Wildlife Fund Canada. 376:Avian Conservation and Ecology 1: 1263:Fatal Light Awareness Program 791:10.1590/0001-3765202020180745 304:with antenna towers and masts 1127:. Toronto.ca. Archived from 942:10.1016/j.biocon.2019.108358 887:10.1016/j.envpol.2020.116136 846:10.1007/978-3-642-74542-3_18 705:10.1371/journal.pone.0053371 1285:, American Bird Conservancy 1156:September 27, 2011, at the 1325: 990:Journal of Applied Ecology 292:Ecological light pollution 266:Monitoring and legislation 65:Window collision variables 18:Bird–skyscraper collisions 1186:. GovTrack.us. 2011-04-15 1029:. Cambridge Univ. Press. 1025:Alerstam, Thomas (1990). 413:10.2134/agronmonogr55.c4 389:10.5751/ace-00568-080206 930:Biological Conservation 875:Environmental Pollution 739:Northeastern Naturalist 616:10.1650/condor-13-090.1 548:10.1093/condor/48.6.278 501:10.1196/annals.1439.015 405:Urban Ecosystem Ecology 575:Alonso, J. A. (1999). 550:(inactive 2024-09-12). 250: 219: 185: 147:Golden-winged Warblers 95: 39:Bird–window collisions 35: 27:Problem in urban areas 329:"Why Birds Hit Glass" 272:New York City Audubon 248: 217: 183: 123:Bay-breasted Warblers 85: 33: 1283:Bird-friendly Design 840:. pp. 269–280. 751:10.1656/045.016.n312 159:Worm-eating Warblers 1268:Lights Out New York 977:. pp. 132–140. 696:2013PLoSO...853371H 493:2008NYASA1134..233D 310:with cars or planes 176:Building properties 100:species composition 78:Susceptible species 251: 232:Weather conditions 220: 186: 161:at high-rises and 135:Blackpoll Warblers 96: 36: 1036:978-0-521-32865-4 855:978-3-642-74544-7 579:. pp. 57–82. 422:978-0-89118-181-1 356:978-0-942015-03-4 88:common kingfisher 16:(Redirected from 1316: 1250: 1249: 1247: 1246: 1226: 1220: 1219: 1217: 1216: 1201: 1195: 1194: 1192: 1191: 1180: 1174: 1173: 1166: 1160: 1149: 1143: 1142: 1140: 1139: 1133: 1126: 1118: 1112: 1111: 1109: 1108: 1093: 1087: 1086: 1075:10.1676/08-118.1 1058: 1049: 1048: 1022: 1016: 1015: 1013: 985: 979: 978: 968: 962: 961: 921: 915: 914: 866: 860: 859: 833: 827: 826: 810: 804: 803: 793: 769: 763: 762: 734: 728: 727: 717: 707: 675: 664: 663: 652:10.1676/07-075.1 635: 629: 628: 618: 594: 581: 580: 572: 566: 565: 559: 551: 527: 521: 520: 476: 461: 460: 444: 427: 426: 400: 394: 393: 391: 367: 361: 360: 342: 333: 332: 325: 155:Painted Buntings 21: 1324: 1323: 1319: 1318: 1317: 1315: 1314: 1313: 1289: 1288: 1259: 1254: 1253: 1244: 1242: 1228: 1227: 1223: 1214: 1212: 1203: 1202: 1198: 1189: 1187: 1182: 1181: 1177: 1168: 1167: 1163: 1158:Wayback Machine 1150: 1146: 1137: 1135: 1131: 1124: 1120: 1119: 1115: 1106: 1104: 1095: 1094: 1090: 1060: 1059: 1052: 1037: 1024: 1023: 1019: 987: 986: 982: 970: 969: 965: 923: 922: 918: 868: 867: 863: 856: 835: 834: 830: 812: 811: 807: 771: 770: 766: 736: 735: 731: 677: 676: 667: 637: 636: 632: 596: 595: 584: 574: 573: 569: 552: 529: 528: 524: 478: 477: 464: 446: 445: 430: 423: 402: 401: 397: 369: 368: 364: 357: 344: 343: 336: 327: 326: 322: 317: 288: 268: 243: 234: 226: 212: 210:Light emissions 203: 178: 165:at residences. 151:Canada Warblers 131:Red-eyed Vireos 80: 67: 41:(also known as 28: 23: 22: 15: 12: 11: 5: 1322: 1320: 1312: 1311: 1309:Urban wildlife 1306: 1301: 1299:Bird mortality 1291: 1290: 1287: 1286: 1280: 1275: 1270: 1265: 1258: 1257:External links 1255: 1252: 1251: 1221: 1196: 1175: 1161: 1144: 1113: 1088: 1069:(2): 314–321. 1050: 1035: 1027:Bird migration 1017: 980: 963: 916: 861: 854: 838:Bird Migration 828: 805: 764: 745:(3): 455–470. 729: 665: 646:(3): 550–564. 630: 582: 567: 522: 487:(1): 233–266. 462: 428: 421: 395: 362: 355: 334: 319: 318: 316: 313: 312: 311: 305: 299: 294: 287: 284: 267: 264: 242: 239: 233: 230: 211: 208: 202: 199: 177: 174: 170:House Sparrows 157:at low-rises, 140:Cedar Waxwings 79: 76: 66: 63: 51:window strikes 26: 24: 14: 13: 10: 9: 6: 4: 3: 2: 1321: 1310: 1307: 1305: 1302: 1300: 1297: 1296: 1294: 1284: 1281: 1279: 1276: 1274: 1271: 1269: 1266: 1264: 1261: 1260: 1256: 1240: 1236: 1232: 1225: 1222: 1211:on 2013-06-16 1210: 1206: 1200: 1197: 1185: 1179: 1176: 1171: 1165: 1162: 1159: 1155: 1152: 1148: 1145: 1134:on 2013-06-03 1130: 1123: 1122:"Environment" 1117: 1114: 1102: 1098: 1092: 1089: 1084: 1080: 1076: 1072: 1068: 1064: 1057: 1055: 1051: 1046: 1042: 1038: 1032: 1028: 1021: 1018: 1012: 1007: 1003: 999: 995: 991: 984: 981: 976: 975: 967: 964: 959: 955: 951: 947: 943: 939: 935: 931: 927: 920: 917: 912: 908: 904: 900: 896: 892: 888: 884: 880: 876: 872: 865: 862: 857: 851: 847: 843: 839: 832: 829: 824: 820: 816: 809: 806: 801: 797: 792: 787: 784:: e20180745. 783: 779: 775: 768: 765: 760: 756: 752: 748: 744: 740: 733: 730: 725: 721: 716: 711: 706: 701: 697: 693: 690:(1): e53371. 689: 685: 681: 674: 672: 670: 666: 661: 657: 653: 649: 645: 641: 634: 631: 626: 622: 617: 612: 608: 604: 600: 593: 591: 589: 587: 583: 578: 571: 568: 563: 557: 549: 545: 541: 537: 533: 526: 523: 518: 514: 510: 506: 502: 498: 494: 490: 486: 482: 475: 473: 471: 469: 467: 463: 458: 454: 450: 443: 441: 439: 437: 435: 433: 429: 424: 418: 414: 410: 406: 399: 396: 390: 385: 381: 377: 373: 366: 363: 358: 352: 348: 341: 339: 335: 330: 324: 321: 314: 309: 306: 303: 300: 298: 295: 293: 290: 289: 285: 283: 279: 275: 273: 265: 263: 260: 256: 247: 240: 238: 231: 229: 224: 216: 209: 207: 200: 198: 194: 190: 182: 175: 173: 171: 166: 164: 163:Wood Thrushes 160: 156: 152: 148: 143: 141: 136: 132: 128: 124: 120: 116: 112: 108: 103: 101: 93: 92:Alcedo atthis 89: 84: 77: 75: 73: 64: 62: 60: 56: 55:United States 52: 48: 47:aviation term 44: 40: 32: 19: 1243:. 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Index

Bird–skyscraper collisions

aviation term
United States
Canada
taxon

common kingfisher
species composition
warblers
thrushes
hummingbirds
vireos
Bay-breasted Warblers
Ovenbirds
Red-eyed Vireos
Blackpoll Warblers
Cedar Waxwings
Golden-winged Warblers
Canada Warblers
Painted Buntings
Worm-eating Warblers
Wood Thrushes
House Sparrows



ultraviolet
frit
New York City Audubon

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